Light pollution reduces activity, food consumption and growth rates in a sandy beach invertebrate☆
Graphical abstract
Introduction
Natural light sources (sunlight and moonlight) play a fundamental role on an array of organisms and ecological processes (Gaston et al., 2012). For example, the light of stars provides essential signals for long distance migration of birds (Åkesson et al., 2001) as well as direction to nocturnal insects (Verheijen, 1985). Sunlight and moonlight are also key drivers of circadian rhythms (Scapini et al., 1997), nocturnal migrations of pelagic organisms (Ringelberg, 1999) and modulators of predator-prey interactions (e.g., Clarke, 1983, Kotler et al., 1991), among many other processes. In this context, human alteration of natural light cycles is likely to lead to important effects on biological processes and diversity. A 6% annual increase in worldwide artificial lighting due to the rise of human infrastructure and activity (Hölker et al., 2010), has triggered concerns about the potential impact of this stressor on a variety of organisms and communities (Longcore and Rich, 2004, Hölker et al., 2010, Gaston et al., 2012).
Ecological light pollution (hereafter ELP) is the “artificial light that alters the natural patterns of light and dark in ecosystems” (Longcore and Rich, 2004). Among the best understood effects of ELP are those documented for sea turtle orientation (Peters and Verhoeven, 1994), facilitated detection of prey by predators (Eisenbeis and Hassel, 2000, Kolligs, 2000, Rydell, 1992, Frank, 2006), visual interference (Le Corre et al., 2002), and alteration of feeding behaviors (Bird et al., 2004). As of 2010, over 20% of the world coastlines (excluding Antarctica) were exposed to some level of artificial lightning (Davies et al., 2014). In these systems, sandy beaches represent over 80% of the ice-free coastline (Short, 1999, Bascom, 1980), and yet, the potential effects of ELP on these habitats remain virtually unknown (Schlacher et al., 2016). Sea turtles are, again, an exception (Witherington and Martin, 2000): we know for example that artificial light networks inhibit turtle nesting in sandy beaches and disorient their hatchlings (Peters and Verhoeven, 1994).
Crustacean amphipods of the family Talitridae are, in terms of biomass and abundance, among the dominant organisms in the upper levels of temperate sandy beaches (e.g., Dahl, 1952, Scapini et al., 1997, Jaramillo et al., 2002). These amphipods play an important community role and accelerate the decomposition of stranded macroalgae wracks (Lastra et al., 2008, Olabarria et al., 2009, Duarte et al., 2010, MacMillan and Quijon, 2012). Most amphipods display distinctive circadian rythms entailing the active search for food during the night hours and the burying in the upper and mid intertidal sediments during daylight (Jaramillo et al., 2003, Dugan et al., 2004, Duarte et al., 2009, Duarte et al., 2014). Among other cues, Talitrid amphipods rely on visual stimuli like the sun and the moon for their orientation and circadian rythms (Mezzetti et al., 2010, Scapini, 2006, Nardi et al., 2000, Scapini et al., 1997). Hence, it is reasonable to think that the widespread growth of artificial lightning would likely alter their activity patterns as well as their feeding behavior.
The Talitrid amphipod Orchestoidea tuberculata is among the numerically dominant species in the upper intertidal zone of exposed sandy beaches of central and southern Chile in the southeastern Pacific (Varela, 1983, Jaramillo et al., 2000, Jaramillo et al., 2003). Activity patterns in this species change along the life cycle: while juveniles are active along the 24 h cycle (Jaramillo et al., 1980), subadults are more active at dusk and night, and adults are strictly nocturnal. Hence, based on their abundance and well known activity patterns, adult O. tuberculata represent ideal models for the study of the ELP in the central Chile coastline. Surprisingly though, little has been done about it with the exception of a survey conducted by Giaconni (2006). This author found abundant populations of this species in all but one sandy beach system which, coincidentally, was the only one exposed to ELP. However, no experimental studies to date have tested the relationship between ELP and any relevant aspects of the ecology of this species. Our study aims to fulfill that knowledge gap by experimentally assessing the influence of ELP on the locomotor activity and feeding ecology of adult O. tuberculata.
Section snippets
Field experiments
We conducted field experiments in Las Docas (33°08′19.5″S; 71°42′21.2″W) and Quintay (33º11′00″S; 71º41′10″W) sandy beaches, in central Chile (Fig 1). We chose these sites because they are far enough from large urban centers as to provide full dark conditions and support large populations of O. tuberculata (Duarte unpublished). In December 2013, we deployed two experimental arrays in Las Docas (Fig. 1). Each array included three rows of 3 containers each holding 20 g of fresh pieces of the alga
Field experiments
In the first experiment (2013; alternating light-darkness), we found amphipod activity at least once in all patches in ambient conditions (not exposed to artificial light). In contrast, none of the patches located at 3 m and only half of those located at 6 m from the light source presented O. tuberculata activity when exposed to light. The best AICc model included additive effects of treatment and distance (Table 1, Table S1). In the second field experiment (2014), the effect of artificial
Discussion
Ecological light pollution is an emerging threat for biodiversity in general (Perkin et al., 2011, Gaston et al., 2013) and for sandy beach organisms in particular (Schlacher et al., 2016). Nevertheless, to date the effects of ELP on sandy beach organisms (other than sea turtles) have remained largely unexplored (Schlacher et al., 2016). The handful of studies that have addressed ELP impacts on beach invertebrates, have done so by applying correlative analyses (e.g., Giaconni, 2006, González
Acknowledgments
The authors are grateful of Francesca Carrion and Nicole Zúñiga for their valuable assistance during the experiments. This study was supported by Dirección General de Investigación, Universidad Andres Bello (Proyecto DI no 302-13 to C. D.). The Millennium Nucleus Center for the Study of Multiple-Drivers on Marine Socio-ecological Systems funded by MINECON NC120086 also funded this work during its final stage. PAQ acknowledges the continued support from UPEI and the Natural Sciences and
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